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Malaysia and Singapore
Saifullah Arifin Jaaman and Elizabeth Taylor made significant contribution to the sections on Malaysia
and Singapore respectively. Thanks are also due to the Malaysian Department of Fisheries for access to
their records.
Distribution and Abundance
Dugongs occur in Malaysian waters including the waters of Peninsula Malaysia and the waters off the
state of Sabah in East Malaysia (Figure). However, there are no estimates of the size of the dugong
population in either area.
Peninsula Malaysia and Singapore
Dugongs were rarely reported in the waters of Peninsula Malaysia and Singapore prior to the 1990s. The
few reports were from the coastal waters of Johor and Singapore. Records of dugongs in Singapore
waters go back as far as 1821, but no quantitative data on population size and distribution are available
(see Sigurdsson and Yang 1990). Dugongs were considered nearly extinct by the 1970s and were largely
unheard of among Singaporeans, with the exception of a small number of concerned and interested
people (Chew 1988). Older records from the early parts of this century include sightings from Pulau
Tekong or the Changi area including Telok Paku and Tanah Merah beach, however, both these beaches
are now reclaimed land. Sigurdsson and Yang (1990) report evidence of a viable breeding population in
the Johor River estuary. Stranding reports from 1974 to 1989 include records of three young animals
which suggests that dugongs were breeding in these waters at that time. In more recent times, most
sightings have occurred northeast of Singapore around Ubin and Tekong islands as well as around the
southern islands, and off the Changi area (Taylor et al. 1997; Douaze pers comm. 1998).
There is strong anecdotal evidence to suggest that dugongs are resident in the Johor -Singapore region.
The islands off the east coast of Johor support the largest known seagrass beds in Peninsula Malaysia
(M. Kushairi pers comm. 1999) and at least 17 adults and one calf were sighted during a helicopter
survey of Pulau Sibu Hujong (2o99’N , 104 o 007’E) and nearby Pulau Besar and Pulau Rawa conducted
by Malaysian Fisheries off the east coast of Johor in May 1999 (M. Kushairi, Mansor Mat Isa and H.
Marsh unpublished data). These islands are in the Pulau Tinggi Marine Park (check this). Although the
occurrence of seagrass in Johor Strait was very restricted in 1999, a total of at least 10 dugongs were
found stranded or caught in fishing nets in this region between 1994 and 1999 (Marsh 1999). In addition,
three dugongs were sighted off Pasir Puteh (1o25.54’N, 103 o57.66’E) during an aerial survey in March
1999 (Malaysian Fisheries Department 1999). Another dugong was sighted on the west side of Pulau
Rawa Johor Strait (1 o29.31’N, 104 o 007.88’ E) and presumed dugong feeding trails were seen in a
meadow of Halophila ovalis at the mouth of Sungai Boh off Sungai Pulai in Johor Strait during the May
1999 survey (M. Kushairi, Mansor Mat Isa and H. Marsh unpublished data). Further evidence for
dugongs being resident in the Johor Straits comes from genetic analysis. Two immature males captured
in May 1999 were first order relatives. If the animals using Johor Strait were vagrants from the islands
off the east coast of Johor, the chances of brothers using the same area nearly two months apart would be
low (M. Kushairi, Masor Mat Isa and H. Marsh unpublished data).
The waters of Pulau Lankawi on the west coast of Peninsula Malaysia is also believed to be an area
frequented by dugongs. Fishermen in this area reported sighting dugongs in 1999 (Malaysian Fisheries
Department 1999).
East Malaysia please check with Islabel whether this the right generic name
There have been numerous sightings of dugongs by fishermen in Sabah including Kudat, Sandakan, and
Semporna (Jaaman et al. 1997). Other areas with possible viable populations are at Kota Kinabalu on the
west coast. In 1999, four dugong strandings occurred near Kota Kinabalu (Figure ) and a sighting of a
live adult for a period of more than a week was reported within the Kota Kinabalu harbour (Jaaman
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2000). The occurrence of dugongs ner Kota Kinabalu is attributed to the seagrass in Sepangar Bay,
Tunku Abdul Rahman Marine Park, and Tanjung Badak. Since January 2000, there have been two live
sightings of dugongs reported in Kota Kinabalu. In August 2000, a 2m dugong was found dead on the
beach of Manukan Island (Tunku Abdul Rahman Marine Park). In May 2000, aerial surveys conducted
along the coast of Sabah, by members of the Malaysian Marine Mammals and Whale Shark Working
Group, sighted four dugongs; three in Kudat and one in the Federal Territory of Labuan (Jaaman pers
comm. 2000). All dugongs were sighted in shallow waters and were feeding on seagrass close to shore.
Kudat is known to have extensive seagrass beds. There have also been two reports of incidental catches
of dugongs in gillnets in the area as of August 2000.
Prior to these recent sighting and strandings, dugongs have been reported to occur near Muara
breakwater, Brunei (Elkin 1992), Tanjong Datu, Sarawak (Bank 1931), and Tambisan Island, Sabah
(Dollar et al. 1997), where they were commonly believed to have been hunted to near extinction. A
dugong skull, collected from Banggi Island off Kudat in 1999, is kept at the Universiti Malaysia Sabah
(Jaaman 1999).
Threatening Processes
Historical dugong hunting, incidental catch from fishing activities, habitat loss including loss form land
reclamation, pollution from palm oil plantations and sedimentation, are the main threats to dugong
populations in this region.
Habitat Loss and Degradation
The southeast Asian region is being rapidly developed and 70% of its human population is living on or
near the coast. Coastal development brings pollution and causes the loss or degradation of marine
habitats including seagrass
Peninsula Malaysia and Singapore
Kushairi (1992) recorded eight species of seagrass at the following locations in the coastal waters of
Peninsular Malaysia: west coast north to south – Tanjong Rbu, Telok Ewa, Beting Tengak, Teluk
Nipah, Telok Kemang; East coast north to south – Kuala Sotiu, Pulau Tengah, Palau Besor, Pulau
Tinggi, Pulau Sibu (Figure)
In Singapore seven seagrass species have been recorded but no extensive beds (Loo et al. 1994). The
seagrass food of the dugong in captivity in Underwater World Singapore Aquarium is imported from
Indonesia. Seagrass meadows can also be found around Pulau Tekong and Ubin, but many meadows in
the south have been reclaimed and can no longer support dugong populations (Durville and Taylor
1996). Some seagrass beds have been destroyed off Pulau Tekong and Changi beach where extensive
land reclamation has taken place (Chew 1996). Land reclamation stirs up silt that can smother coral reefs
and seagrass meadows, which are heavily dependent on light for photosynthesis and growth. The Johor
River estuary, where a viable dugong population apparently still occurs (see above), is targeted for major
development. This means further reclamation of shallow water areas and the destruction of seagrass
beds.
Information from the necropsies of five dugongs found near the mouth of the Johor River in March 1999
suggests that starvation contributed to the death of at least two animals and that a third died of
septicaemia (Marsh 1999).
East Malaysia
East Malaysia also has seagrass habitats with 10 species identified (Japar, 1994). Little is known about
their current status although extensive coastal development is occurring in many areas and this is likely
2
to have adverse impact on the seagrass beds since there is little general appreciation of the value, even
for economically important industries such as fishing.
The development of Sandakan into a major industrialised town in Sabah (Figure ) may have a
detrimental effect on local seagrass. Pollution of waterways contributes to dugong habitat loss. In the
past 10 years many jungles on the inner side and upstream of the rivers in the Sandakan and Beluran
areas (Figure ) have been transformed to cultivation lands including large scale palm oil plantations.
During the wet season (November to February), rain washes the insecticides and fertilisers used in
farming practices into the rivers and bays. Sedimentation also increases water turbidity. It is believed
that the runoff from a severe flood in 1955 in the state of Sabah that decreased the water salinity in
Sandakan Bay to zero for a few weeks was responsible for a large-scale seagrass dieoff (Jaaman et al.
1997b).
Fishing Pressure
Singapore and Peninsula Malaysia
The fisheries in Singapore waters are genrally small scale largely using hooks and bait (Chew 1996). In
September 1998, a stranded female calf found off the shores of Pulau Ubin, an island northeast of
mainland Singapore, was transferred to Underwater World Singapore (Lin 1999). The calf was found
close to a dead female dugong, assumed to have been her mother, which had been trapped in a net. Other
records of stranded dugongs show signs indicating entanglement in fishing nets (Sigurdsson and Yang
1990).
In addition to the one above, at least five dugongs were captured in fishing nets and fish traps (kelong) in
the Johor Straits between 1994 and 1999 (Malaysian Fisheries Department records)
East Malaysia
Historically, dugongs were mainly hunted for their meat, which is considered a delicacy and is
considered by some to be more delicious than beef. Today, almost all catches are accidental, although
sometimes fishers in Sabah take advantages of opportunities catch dugongs. Dugongs can be caught in
kelong and fishnets such as gill nets, beach and purse seines, and in bag nets. One live adult dugong was
found trapped and later released from a kelong in Kampung Gas, Sandakan, Sabah in 1994 (Fisheries
News No. 15, September 1994). There are also anecdotal reports of dynamite fishing occurring in the
waters of Sabah, which may cause dugong mortalities (UNEP 1996 and see above). In some areas,
dynamite fishing is also being used to hunt dugongs and dolphins (Jaaman pers comm. 2000). A dugong
stranding was also reported in August 1999 on the beach of Pulau Papan, Federal Territory of Labuan
(Jaaman et al. 1999). According to the post-mortem conducted by the Veterinary Department, the 2.6 m,
250 kg female did not die of starvation; a lack of external injuries indicated that the death may have
resulted from dynamite fishing.
Fishermen and/or local villagers from Sandakan and Labuk/Beluran Bays, Sabah, reported during
interview surveys in 1997, that they had seen either dolphins or dugongs within the vicinity of their
villages (Jaaman et al., 1997b). Sandakan and Labuk Bays serve as major fishing grounds for artisanal
fishermen in the area. Seven of the nine fishing villages interviewed in Sandakan Bay reported directed
and/or incidental marine mammal (Irrawaddy dolphins and dugongs) and turtle takes, whereas only three
of the eight fishing villages visited in Labuk Bay reported takes. In both bays, villagers indicated that
dugong populations have declined significantly in the past few decades and animals are no longer, or
only very rarely seen in the areas where they were once common (Jaaman et al., 1997b).
Indigenous Use and Hunting
3
Peninsula Malaysia and Singapore
Chew (1996) reports that dugong hide was used as leather, which was appreciated for its good quality.
The tusks were carved into knife handles and the “congealed mucous secretion of the eye-lid” was
believed to be a powerful love potion (Chew 1996). Dugongs were traditionally hunted from small boats
with harpoons and then “played” until exhausted by means of a stout line which had previously been
fastened to the harpoon head (Sigurdsson and Yang 1990). Approximately 12 dugongs per year were
caught in the vicinity of Pulau Tekong. Dugong meat used to fetch a good price as the meat is much
esteemed by the Chinese and Malays, as a luxury generally eaten only at feasts (Sigurdsson and Yang
1990). The Malaysian Fisheries Department records of dugongs indicate that dugongs were hunted at
Kg. Penda Laut in Johor in the 1970s.
East Malaysia
Many local villagers and fishermen around Sabah associate dugongs with various superstitious beliefs
and some will release the animal when incidentally caught. Dugongs were considered mysterious and
human-like, although some described them as monstrous. Some say that their body parts have medicinal
powers. Reference ask Isabel Dugongs were mainly hunted for their meat, which is considered a
delicacy and is said to be more delicious than beef. The animals were hunted using harpoon, javelin and
nets in coastal areas off Sabah and Johor. Anyi and Jaaman (in press) report that in Semporna, east coast
of Sabah, the Bajau Laut (Sea Nomads) consider dolphin and dugong meat a delicacy and it has been a
source of red meat for them for years. They hunt dugongs silently at night using spears and rowing boats
with help from “pawang”, a medicine man that reads the spells. The meat is either cooked or dried, but
many of them prefer the animals' blubber, regarding it as the most delicious part. Dugongs caught are cut
into small pieces before being sold to the villagers. A three-to five-inch piece of dugong meat fetches
RM 5 (US$$ check Isabel) and a whole dugong can fetch up to RM 60 to RM 100 (US$ ), depending on
its size.
In the Sandakan Bay area, Sabah, dugongs were also hunted at night using spears tied to the bow of the
boat with a rope about 100 m long. According to local elder villagers interviewed by Jaaman et al.
(1997), an average of one dugong a month was caught in the Sandakan area before 1955. Reports of
dugongs sightings or killings in this area ceased by 1975. However, the villagers believe that the animals
are still present, but in very small numbers. This is supported by the report of a dugong found trapped in
a kelong in Kampung Gas mentioned above. In addition, many older fishermen interviewed in Labuk
stated that Kaniogan, Tg. Semangat at Pulau Jambongan and Pulau Nunuyan were some of the major
dugong hunting areas before and during the 1970s (Jaaman et al. 1997). Dugongs were believed to have
been hunted to near extinction near Muara breakwater, Brunei Tanjong Datu, Sarawak (Bank 1931), and
Tambisan Island, Sabah.
Boat-related Impacts
Peninsula Malaysia and Singapore
The increasing popularity of leisure motor-boats poses a threat to dugongs in Singapore and Malaysia. In
addition to the risk of collision, heavy boat traffic is likely to have an effect on dugong behaviour,
forcing them to leave busy areas or modifying their feeding habits. There is evidence that some stranded
dugongs may have been victims of boat propeller strikes (Sigurdsson and Yang 1990; Jaaman pers
comm. 2000). For example, severe propeller wounds were found on the back of an animal which died in
Febraury 1999 (Malaysian Department of Fisheries records). It is not known whether these wounds we
inflicted before or after death.
East Malaysia
4
In August 2000, a 2m dugong found dead on the beach of Manukan Island (Tunku Abdul Rahman
Marine Park) was believed to have been hit by a boat propeller. The fluke was severely damaged and
almost cut off.
Conservation Measures Already in Place
Legislation
Malaysia
Dugongs are a protected species in Malaysia under:
 The Wildlife Protection Act 1972 – all of Malaysia
 The Fisheries Act 1985, Part VI – aquatic mammals in Malaysian Economic Exclusive Zone
 The Wildlife Conservation Enactment 1997 – Sabah
 The Wildlife Protection Ordinance 1990 - Sarawak
Article 27 of the Fisheries Regulation 1985 specifies that endangered species should be released if they
are found entangled in nets or stranded on shore; in cases where animals are found dead, reports should
be made to relevant agencies for further actions.
Info on marine parks here
Research
Peninsula Malaysia
Kushairi (1992) conducted a manual scuba survey of seagrasses thoughout the coastal waters of
Peninsula Malaysia between mid 1986 and mid 1991. As summarised above, a total of eight seagrass
species were recorded at 10 locations of which .. are currently in marine parks, especially check status of
islands wher dugong sighted off east Johor are they in the Pulau Tingii Marine Park
Awating advice from Max Harriman to Helene
Singapore
A Singapore Wild Marine Mammal Survey (SWiMMS) program run by the Dolphin Study Group of the
Tropical Marine Science Institute, National University of Singapore was established in 1996 to study the
ecology, behaviour, and health of local marine mammals. The objective is to develop recommendations
for integrating coastal marine utilisation with responsible conservation of the natural marine resources
on which marine mammals depend. Marine mammal distribution information is obtained from the public
through a sighting program, boat surveys and stranding information (see Durville and Taylor 1996).
Sighting forms have been distributed to divers, sailing clubs, the Maritime and Port Authority of
Singapore ferry captains, and many other individuals.
East Malaysia
There has been little research on marine mammals in Malaysia. Historically, records of sightings and
strandings have been poorly documented. In early 1996, the Marine Mammals and Whale Shark
Research and Conservation Programme of Universiti Malaysia Sabah (UMS) was initiated (Jaaman &
Palaniappan 1998). Members of the Marine Mammals and Whale Shark Working Group conduct
interviews, habitat surveys and other basic studies related to the biology, ecology, and behaviour of
dugongs and cetaceans to determine the presence, distribution and population status of marine mammals
in the country and the impact of human activities on the species. The specific objectives of the
programme are to:
5
1.
2.
3.
4.
5.
6.
7.
Identify and document marine mammals present in Malaysian waters, particularly in Sabah and
Sarawak.
Determine the distribution, abundance, ecological aspects, and economic importance of these
animals in the area.
Identify the nature and extent of human impacts including fisheries interactions and habitat
degradation.
Initiate studies on selected species.
Investigate areas where suitable management policies can be implemented to protect vulnerable
resources.
Promote marine mammal awareness in both academia and the general public.
Be the responsible body for collaboration and scientific networking with other participating
countries.
In addition, various government agencies and private sector oganisations are helping to study, document,
and protect marine mammals in Malaysia. Most of these agencies are members of the Malaysian Marine
Mammals and Whale Shark Working Group. In 1996, the University of Malaysia Sabah (UMS)
approved a short-term grant to initiate a preliminary survey of marine mammals and whale sharks in
Sabah. In 1997, the Ministry of Science, Technology and Environment Malaysia provided funding for
three years to UMS to support the Working Group in carrying out a research project titled “An
Integrated Study of Marine Mammals and Whale Sharks in the Malaysian Exclusive Economic Zone”.
Findings from the research project and a technical report are expected in 2001.
The current members of the Malaysian Marine Mammals and Whale Shark Working Group include:
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
Universiti Malaysia Sabah Secretariat
Universiti Malaysia Sarawak
Universiti Putra Malaysia Terengganu
Department of Fisheries, Malaysia
Department of Fisheries, Sabah
Department of Wildlife, Sabah
Sabah Parks
Sabah Museum
World Wide Fund for Nature, Malaysia
Borneo Divers & Sea Sports (Sabah) Sdn. Bhd.
The Marine Mammals and Whale Shark Working Group prepared a research and development plan for
marine mammal and whale shark research in Malaysia that listed several projects (Jaaman et al. 1997a).
Phase I on the plan includes the following projects:
1. Increasing public awareness on the conservation of marine mammals by giving talks, exhibitions
and slide shows, especially to students and people who live in coastal areas or work at sea. Also, to
encourage the general public (e.g., marine ecotourism industrialists) to participate in documenting
marine mammal occurrences.
2. Gathering information and establishing a database to manage sightings, observations and survey
records in the country. Continuous data analysis and results will be published for public viewing.
3. Documenting, salvaging and managing specimens (tissues and skeletons) of dead animals for future
research and public viewing.
4. Conducting research expeditions and field surveys to identify species present in Malaysian waters
and study the biology, ecology and human related matters of resident species, especially in the
coastal areas where many reports of the animals have occurred.
5. Organising several seminars and workshops on marine mammals present in Malaysian waters
participated by representatives from various agencies concerned, the public, and also experts from
overseas.
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6. Initiating local universities to join the programme and identifying local postgraduate students to be
involved in research under a graduate assistant scheme. Collaborative research with foreign
scientists should also be encouraged for staff development.
The projects listed above have been initiated by the UMS but are currently confined to the state of
Sabah. The marine mammal stranding network (project 3) has not been fully developed and is not
operational yet.
Management
Malaysia
There is no management plan for dugong populations in Malaysia (Ridzwan Adbul Rahman pers comm.
1998). The implementation of existing laws are addressed by the regional and local Department of
Wildlife and Fisheries offices which are both members of the Marine Mammals and Whale Shark
Working Group. The Working Group also produces information and education materials. Education
campaigns targeted towards fishermen, students, and law enforcers in critical areas, were conducted in
Sabah and other states in Malaysia. The publicity generated by the capture, display and death of the
dugong calf held in a kelong in Johor Strait and subsequently released in 1999 resulted in a greatly
increased public awareness in the region about dugongs. This awareness is enhanced by the display of a
dugong calf at Underwater World Singapore.
Suggested Conservation Measures
Research

The Malaysian Cabinet has directed the Secretary General of the Ministry of Science, Technology
and the Environment to ensure that research is undertaken on dugongs. We recommend that the
highest priority should be given to surveys to determine the distribution and relative abundance of
dugongs and their habitats throughout the waters of Peninsula Malaysia and Singapore and East
Malaysia (especially Sabah). Priority areas should be selected with input from relevant stakeholders
using criteria such as: (1) biodiversity importance especially areas of known dugong and seagrass
abundance (such as the east cost of Johor, Pulau Lankawi and the east coast of Sabah), (2) other
relevant ecological data, (3) the degree of local commitment, and (4) the probability of success in
sustainable management of seagrasses in the context of the critical social and environmental factors
affecting the proposed priority areas.

We also suggest that interview surveys should be conducted simultaneously to assess the knowledge
of the local people and the fishing communities with regard to dugong protection, their biology,
seagrass distribution and fisheries. The magnitude of directed and incidental takes of dugongs for
local consumption should be investigated as part of the interview surveys. The impacts of dugong
bycatch in fishing gear (especially gillnets and traps) needs to be investigated and documented.
Emphasis should be on the priority areas identified as suggested above.

These data should be used to provide decision makers and local communities with data essential for
coastal zone management in general and dugong and seagrass conservation in particular. These
activities are likely to be most effective if community-based.

Consideration should be given to extending the cooperative sea turtle research program that has been
developed between the Philippines and Sabah (UNEP 1996) to include dugongs and coastal
cetaceans.
7
Management

Collaboration in research and conservation efforts between relevant agencies including the
Malaysian Department of Fisheries, other relevant national and state government departments,
relevant universities, NGOs and local communities should be encouraged for effective protection of
dugong populations.

Consideration should be given to Malaysian authorities working in cooperation with the Philippine
Government to protect dugongs, especially around the Sulu Sea and Palawan, with the Singapore
Government to protect dugongs in the Johor region. The Indonesian and Singaporean governments
could develop a cooperative initiative to protect dugongs in the Strait of Malacca

A culturally public information campaign regarding dugongs and their habitats could build on the
recent high public profile of the dugong. A dugong and seagrass Public Information Centre at the
Pulau Tingii Marine Park could be a focus for this campaign.
Conclusions
Recent information suggests that populations of dugongs exist at several sites in the coastal waters of
Peninsula Malaysia and East Malaysia. The profile of the dugong is currently high and the Malaysian
Government is committed to a program of dugong research and management.
8